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SUSTAINABLE DEVELOPMENT OF EXPORT- ORIENTATED FARMED SEAFOOD IN THAILAND A thesis submitted for the degree of Doctor of Philosophy By Arlene Nietes-Satapornvanit Sustainable Aquaculture Research Group Institute of Aquaculture, School of Natural Sciences, University of Stirling Scotland, United Kingdom April 2014

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  • SUSTAINABLE DEVELOPMENT OF EXPORT-

    ORIENTATED FARMED SEAFOOD IN THAILAND

    A thesis submitted for the degree of Doctor of Philosophy

    By

    Arlene Nietes-Satapornvanit

    Sustainable Aquaculture Research Group

    Institute of Aquaculture, School of Natural Sciences, University of Stirling

    Scotland, United Kingdom

    April 2014

  • i

    D E C L A R A T I O N

    This thesis has been composed in its entirety by the candidate, except where specifically

    acknowledged. The work described in this thesis has been conducted independently and

    has not been submitted for any other degree.

    Signature: ______________________________________________________

    Date: __________________________________________________________

  • ii

    ABSTRACT

    Sustainable development of export-orientated farmed seafood in Thailand is a major

    issue which can impact local stakeholders as well as global food security. The major

    species taken into consideration in this research were initially the Pacific white shrimp

    (Litopenaeus vannamei), Nile tilapia (Oreochromis niloticus), giant freshwater prawn

    (Macrobrachium rosenbergii), and striped catfish (Pangasianodon hypophthalmus). After

    which more focus was placed on Pacific white shrimp, which is Thailand’s major cultured

    seafood being traded for export, and tilapia, which has potential for export but also

    enjoying a good domestic market demand.

    Actors or stakeholders directly and indirectly involved in aquaculture value chains may

    have their own perceptions about sustainability affecting their operations, as various

    factors within and outside their own systems could affect these perceptions. This could

    lead to different efforts in responding to these factors to make their operations

    sustainable.

    Three major areas were covered in this study, namely a) describing the strengths and

    weaknesses of shrimp and tilapia production in Thailand in relation to their export

    potential, b) evaluating the status of compliance to global aquaculture standards of

    shrimp and tilapia farming (covering technical and labour aspects), and c) determining

    perceptions of sustainability across the shrimp and tilapia value chains in Thailand, with a

    focus on the production sector.

  • iii

    A mixed-methods approach was employed to obtain information in the study sites in

    Thailand. Basic field interviews were conducted among 206 shrimp producers in 6

    provinces in the east and south, and 199 tilapia producers in 4 provinces in the west and

    east, in terms of farm operations and perceptions of factors which will affect the

    sustainability of their operations, including generational aspects on future shrimp and

    tilapia farming.

    Key informant interviews were also conducted among other value chain actors (>30) such

    as hatchery/nursery operators, input/service providers, processors/exporters and

    technical/ institutional members to determine whether there are differences in their

    sustainability perceptions.

    In addition, face to face interviews with 18 shrimp farm male and female workers were

    conducted (Thai and migrant workers), as well as with 14 key informants involved in

    shrimp farm labour issues in Thailand, specifically for well-being and working conditions.

    Stakeholders cited environmental (technical), economic, social and institutional (equity)

    aspects of their operations as factors which will affect the sustainability of their

    operations. Disease, product price and water quality were the three most important

    sustainability factors among shrimp farmers, whereas water quality, disease and extreme

    weather conditions were for tilapia farmers. Product price was the most cited by input

    service providers, hatchery operators, shrimp and tilapia producers, and processors.

  • iv

    Both Thai and migrant shrimp farm workers perceived a better or much better-off quality

    of life working in shrimp farms in Thailand than in their previous occupations or status.

    Almost all shrimp farms meet more than what are required under the Thai labour law or

    the global aquaculture standards for human resources. With the importance of migrant

    labour in Thailand, much still needs to be done in terms of assessing the impact of their

    working in Thailand on their families left behind in their own countries, as well as on their

    communities, including status of social protection to avoid exploitation.

    Each stakeholder group strives to achieve sustainability so they can remain in operation in

    the next few years, to survive on the business individually and corporately, and to be the

    best provider of sustainably and ethically produced seafood for the world. The

    compliance to aquaculture global standards and certifications may be considered to

    contribute to the sustainability of operations by improving farm practices thereby

    reducing detrimental impacts on farm and external environments, as well as

    strengthening human relations with in the farm and in the community. However there are

    some aspects of these standards which could eliminate the small players. In this study,

    the large scale farms were more likely to comply with all the standards, followed by

    medium scale, and lastly the small scale farms.

    The differences in perceptions which exist among these stakeholders should be

    understood by every sector and efforts should be made to address them so that there is

    cohesiveness in giving support to achieve sustainable seafood production and trade.

  • v

    ACKNOWLEDGEMENTS

    My heartfelt gratitude to the following who have been part of my PhD journey, and without

    whom this piece of work would not have been completed:

    The research participants (shrimp and tilapia farmers, other value chain actors, farm workers and

    key informants from various government and non-government organisations) in Thailand who

    willingly provided valuable information and knowledge on their operations/ work, and shared

    their ideas and perceptions, during field interviews, workshops and meetings - I hope your voice

    could be heard through this manuscript;

    Prof. David C. Little and Dr. Francis J. Murray for their supervision, guidance, support and

    encouragement to keep thinking, discovering and learning from the ground without forgetting the

    bigger picture; and for the various opportunities to learn from their expertise and experiences, to

    expand and apply ideas to the real world;

    The EU FP7 Sustaining Ethical Aquaculture Trade (SEAT) Project (No. 222889) for funding the

    research; and for additional support from the UoStirling Student Fund and the Churches

    International Student Network-UK;

    The SEAT-Kasetsart University team, led by Dr. Kriengkrai Satapornvanit, and support from Asst.

    Prof. Suriyan Tunkijjanukij, Dr. Prapansak Srisapoome, Dr. Pongtep Wilaipun, Dr. Kulapa

    Supongpan, Dr. Tanaradee Khumya, and the research assistants, esp. Wanwichanee Sritha,

    Kwanklao Srisopha, Laksiri Chomcheun, Jidapa Khatikarn, for their untiring support, guidance in

    local knowledge and wisdom, and perseverance; to SEAT-UoS, esp. to Will Leschen, Lam Phan

    Thanh and Wenbo Zhang, for the fruitful exchanges of ideas, and for sharing references and

    computer skills including helping with formatting this manuscript;

    Prof. Peter Edwards and Prof. Chang Kwei Lin, for the recommendations and wise counsel;

    The Global Café team (Carol, Christine, Geoff, Hamish, Ken & Joan) for the encouragement and

    the coffees; the hospitality of Dely & Raymond Elliot, Ruth & Islwyn Williams, Jacqueline Primrose

    & family, Dave & Dorrit Little; IoAquaculture friends esp. Nattakarn, Winarti, Thao, Cai, Nancy,

    Phuoc, Wanna, Yu-Ching, Udin, Stuart, Mamun for the friendship, & sharing of ideas, coffee, food

    & laughter;

  • vi

    Sa mga imaw ko sa Dungug Kinaray-a kag Balay Sugidanun, sa pagtugro nyo kanakun kang

    kahigayunan nga makapa-utwas kang akun paminsarun kag baratyagun paagi sa pagsulat sa atun

    pinalangga nga hambal;

    My dearest Mom, sisters, and brother, for their love, patience & encouragement; and the

    memory of my Dad, who continues to inspire, encourage and strengthen me;

    My dear husband Key for the greatest support, encouragement and love, so I could continue with

    this endeavour, always reminding me to be strong, and to remain focused to achieve the goal of

    completing this research;

    And to my Lord God, from Whom all blessings flow, for His guidance, protection, healing, and

    enduring love. (Isaiah 41:10).

    … ๆ ...

  • vii

    TABLE OF CONTENTS

    D E C L A R A T I O N .................................................................................................................... i ABSTRACT ............................................................................................................................... ii ACKNOWLEDGEMENTS .......................................................................................................... v TABLE OF CONTENTS ........................................................................................................... vii

    LIST OF FIGURES ............................................................................................................. x LIST OF TABLES ............................................................................................................ xiii LIST OF ACRONYMS ...................................................................................................... xv

    1. CHAPTER 1 Introduction ................................................................................................ 1 1.1. Rationale / Problem statement ........................................................................... 1 1.2. Labour issues ....................................................................................................... 4 1.3. Gender issues ...................................................................................................... 7 1.4. Brief information about the SEAT project............................................................ 9 1.5. Research objectives ........................................................................................... 10 1.6. Key concepts/theoretical framework ................................................................ 11 1.7. Structure of thesis ............................................................................................. 13

    2. CHAPTER 2 General Methodology ............................................................................... 16 2.1. Research activities ............................................................................................. 16 2.2. Sample frame ..................................................................................................... 19 2.3. Definition of farm scale criteria ......................................................................... 21 2.4. Selection of study areas ..................................................................................... 23 2.5. Farmer sampling ................................................................................................ 25 2.6. Integrated farm surveys (IFS) ............................................................................. 27 2.7. Survey instruments ............................................................................................ 28 2.8. Data analysis ...................................................................................................... 31

    3. CHAPTER 3 A systems overview of four commercially important farmed seafood species with an export focus in Thailand ............................................................................. 34

    3.1. Introduction ....................................................................................................... 34 3.2. Trends/historical data ........................................................................................ 42

    3.2.1. Freshwater prawn ................................................................................... 48 3.2.2. Striped catfish ......................................................................................... 53 3.2.3. Tilapia ..................................................................................................... 55 3.2.4. Penaeid shrimp ....................................................................................... 57

    3.3. Importance of seed and hatchery development ............................................... 61 3.4. Emergence of feed industry .............................................................................. 68 3.5. Importance of seafood processing capacity ..................................................... 74

    3.5.1. Shrimp ..................................................................................................... 80 3.5.2. Tilapia ..................................................................................................... 82 3.5.3. Pangasius ................................................................................................ 83 3.5.4. Cold storage ............................................................................................ 85

    3.6. Inter-sectoral learning ....................................................................................... 86 3.7. Seafood intrinsic qualities and issues for domestic and export ........................ 90 3.8. Stakeholder analysis and roles of intermediaries .............................................. 98 3.9. Conclusions ...................................................................................................... 105

  • viii

    4. CHAPTER 4 Shrimp and tilapia farming in Thailand: fulfilling domestic and global market needs ..................................................................................................................... 109

    4.1. Introduction ..................................................................................................... 109 4.2. Research hypothesis/questions ....................................................................... 110 4.3. Scope ............................................................................................................... 112 4.4. Materials and Methods ................................................................................... 112

    4.4.1. Integrated Farm Survey (2010-2011) .................................................... 112 4.4.2. Transition survey (2013) ....................................................................... 114 4.4.3. Data analysis ......................................................................................... 116

    4.5. Results.............................................................................................................. 118 4.5.1. Existing aquaculture certification and standards ................................. 118 4.5.2. Study sites ............................................................................................. 122 4.5.3. Farming systems ................................................................................... 124 4.5.4. Seed source........................................................................................... 130 4.5.5. Stocking size .......................................................................................... 131 4.5.6. Containment systems ........................................................................... 132 4.5.7. Status of farm operations according to selected standards and certifications criteria ........................................................................................... 136 4.5.8. Trends and transition survey: changes occurring among farms ........... 168

    4.6. Discussion ........................................................................................................ 179 4.6.1. Certification, standards and farming systems ...................................... 179 4.6.2. Legal aspects ......................................................................................... 182 4.6.3. Environmental Management: Effluents ................................................ 184 4.6.4. Environmental management: Water quality monitoring ..................... 187 4.6.5. Environmental management: Pond sludge .......................................... 188 4.6.6. Farm management: Feed management ............................................... 191 4.6.7. Energy Use ............................................................................................ 194 4.6.8. Fish welfare issues ................................................................................ 195 4.6.9. Trends and changes .............................................................................. 197

    4.7. Conclusion ....................................................................................................... 198 5. CHAPTER 5 Assessment of the quality of life of shrimp farm workers in Thailand ... 201

    5.1. Introduction ..................................................................................................... 201 5.2. Methodology ................................................................................................... 208

    5.2.1. Survey respondents .............................................................................. 209 5.2.2. Face to face interviews ......................................................................... 213 5.2.3. Key informants ...................................................................................... 218 5.2.4. Survey instruments ............................................................................... 219 5.2.5. Analysis ................................................................................................. 220

    5.3. Results.............................................................................................................. 220 5.3.1. Background of workers ......................................................................... 220 5.3.2. Quality of life of workers in shrimp farms ............................................ 221 5.3.3. Status of compliance to labour standards ............................................ 228 5.3.4. Treatment of workers , especially migrant workers in shrimp farms ... 253 5.3.5. Importance of migrant labour in shrimp farms in Thailand ................. 260 5.3.6. Gender aspects of shrimp farm labour................................................. 265

    5.4. Discussion ........................................................................................................ 267 5.4.1. Quality of Life of shrimp farm workers ................................................. 267

  • ix

    5.4.2. On compliance to global standards and certifications ......................... 270 5.4.3. On treatment of migrant workers by employers .................................. 273 5.4.4. On importance of migrant labour in shrimp farms in Thailand ............ 276 5.4.5. Gender issues ....................................................................................... 277

    5.5. Conclusion ....................................................................................................... 279 6. CHAPTER 6 Shrimp and tilapia value chain actors in Thailand: their perceptions on sustainability ...................................................................................................................... 282

    6.1. Introduction ..................................................................................................... 282 6.1.1. Sustainability definitions/theories ....................................................... 284 6.1.2. Global value chains ............................................................................... 285 6.1.3. Research questions ............................................................................... 287

    6.2. Methodology ................................................................................................... 287 6.2.1. Activity 1. Scoping/exploratory research ............................................. 289 6.2.2. Activity 2. Integrated Farm Survey (IFS) ............................................... 291 6.2.3. Activity 3. State of the System Workshop ........................................... 292 6.2.4. Analysis ................................................................................................. 292

    6.3. Results.............................................................................................................. 294 6.3.1. Generational information ..................................................................... 294 6.3.2. Stakeholders perceptions on sustainability of their operations in the next 1-2 years ...................................................................................................... 298

    6.4. Discussion ........................................................................................................ 306 6.4.1. Generational information ..................................................................... 306 6.4.2. Sustainability perceptions .................................................................... 312

    6.5. Conclusion ....................................................................................................... 317 7. CHAPTER 7 Overall Discussion and Conclusion ......................................................... 319

    7.1. Overall Discussion ............................................................................................ 319 7.2. Reflections on sustainability perceptions of shrimp and tilapia VC actors ..... 330 7.3. Future perspectives and policy implications ................................................... 334 7.4. Critique of the methodology ........................................................................... 336 7.5. Recommendations for future study ................................................................ 338 7.6. Conclusion ....................................................................................................... 340

    8. BIBLIOGRAPHY ............................................................................................................ 343 9. APPENDICES ................................................................................................................ 360

    Appendix 1. Contributions to research design, data collection, data analysis and writing ......................................................................................................................... 360 Appendix 2. Checklist on Scoping and Overview of Production Systems .................. 361 Appendix 3. Details on key informant interviews for sample framing ...................... 364 Appendix 4. Questionnaire for Integrated Farm Survey ............................................ 391 Appendix 5. Questionnaire for Shrimp Transition Survey ......................................... 405 Appendix 6. Questionnaire for Face to Face Survey .................................................. 412 Appendix 7. Checklist for Key Informant Interview on Migrant Labour in Shrimp Farms .......................................................................................................................... 416

  • x

    LIST OF FIGURES

    Figure 1.1 The general research framework ................................................................ 13

    Figure 2.1 Major research activities and timeline undertaken to collect field data .... 17 Figure 2.2 Provinces where the surveys were conducted ........................................... 24

    Figure 3.1 Production of freshwater species from culture systems ............................ 39 Figure 3.2 Volume of exports of freshwater aquaculture species, 2009 to 2013 ........ 41 Figure 3.3 Production and export of tilapia, 2002 to 2013 .......................................... 42 Figure 3.4 Annual production of important aquaculture species ............................... 47 Figure 3.5 Production and growth rate of freshwater prawn in Thailand

    (1989-2009) ........................................................................................................... 51 Figure 3.6 Production and export data of giant freshwater prawn from 2002

    to 2013 .................................................................................................................. 52 Figure 3.7 Production of striped catfish in Thailand and Vietnam .............................. 54 Figure 3.8 Tilapia production and volume of exports for Nile and red tilapia ............. 57 Figure 3.9 Black tiger and white shrimp production in Thailand, 1987 to 2013 .......... 58 Figure 3.10 Food safety incidence reports on Thai shrimp exports to Europe ............ 59 Figure 3.11 Location of feed mills and production areas by species ........................... 70 Figure 3.12 Data map showing the number of seafood processing plants .................. 75 Figure 3.13 Establishment of processing plants and GDP % growth in Thailand ......... 76 Figure 3.14 Quantity and value of shrimp exported, 2008 to 2013 ............................. 81 Figure 3.15 Proportion of shrimp production for domestic and export markets,

    2008 to 2013 ......................................................................................................... 82 Figure 3.16 Roles of independent cold storage companies ......................................... 85 Figure 3.17 Freshwater prawn exported to several countries and value .................... 94 Figure 4.1 Reasons for not responding to shrimp phone transition survey .............. 115 Figure 4.2 Location, scale and number of shrimp farms surveyed, 2010-2011 ......... 122 Figure 4.3 Location, scale and number of tilapia farms surveyed, 2010-2011 .......... 123 Figure 4.4 Tilapia farming systems according to farm scale ...................................... 126 Figure 4.5 Source of shrimp seed by farm scale ......................................................... 130 Figure 4.6 Source of tilapia seed by farm scale .......................................................... 131 Figure 4.7 The number of shrimp ponds according to farm scales ............................ 133 Figure 4.8 Number of ponds and cages in tilapia farms surveyed ............................. 134 Figure 4.9 Uses of ponds and cages in shrimp and tilapia farms by farm scale ......... 135 Figure 4.10 Status of surveyed farms regarding registration with DoF according

    to species and farm scale .................................................................................... 137 Figure 4.11 Ways to treat the effluents from shrimp farms ...................................... 139 Figure 4.12 Status of effluent treatment among tilapia pond farms ......................... 140 Figure 4.13 Methods and routes of discharge of effluents from shrimp and

    tilapia ponds by farm scale ................................................................................. 142 Figure 4.14 Water quality monitoring in shrimp and tilapia farms by farm scale ..... 144 Figure 4.15 Fate of sediments from shrimp and tilapia pond farms .......................... 145 Figure 4.16 Frequency of sediment removal in shrimp and tilapia pond farms

    according to farm scale ....................................................................................... 146

  • xi

    Figure 4.17 Detailed frequency of removing sediments for more than one culture cycle ........................................................................................................ 147

    Figure 4.18 Types of feeds used in shrimp and tilapia culture by farm scales........... 148 Figure 4.19 Shrimp feed manufacturer preference .................................................. 149 Figure 4.20 Tilapia feed manufacturer preference .................................................... 150 Figure 4.21 Record keeping by species and farm scales ............................................ 153 Figure 4.22 Sources of energy in shrimp and tilapia farms by farm scale ................. 154 Figure 4.23 Uses of energy in shrimp and tilapia farms according to farm scales .... 155 Figure 4.24 Precautions taken by farms against predation and poaching by

    farm scale ............................................................................................................ 156 Figure 4.25 Shrimp farms checking PLs by PCR method ........................................... 158 Figure 4.26 Services available to shrimp and tilapia farmers for diagnosing

    disease problems ................................................................................................ 160 Figure 4.27 Pond lining in shrimp farms used for grow-out production

    according to farm scales ..................................................................................... 161 Figure 4.28 A large scale shrimp farm with biosecurity features ............................... 162 Figure 4.29 Fate of stock lost during culture period .................................................. 163 Figure 4.30 Livelihood activities of tilapia farmers .................................................... 164 Figure 4.31 Livelihood activities of shrimp farmers ................................................... 165 Figure 4.32 Changes in shrimp farms during 2005 to 2010 ....................................... 168 Figure 4.33 Changes in shrimp farms in various categories during 2005 to 2010 ..... 170 Figure 4.34 Changes in tilapia farms 2005 to 2010 .................................................... 171 Figure 4.35 Changes in tilapia cage and pond farms during 2005 to 2010 ................ 172 Figure 4.36 General status of shrimp farms two years after IFS ............................... 173 Figure 4.37 General status of tilapia farms two years after integrated farm

    survey .................................................................................................................. 174 Figure 4.38 Changes that occurred in shrimp farms by farm scales ......................... 177 Figure 4.39 Changes in the marketing aspects of shrimp farming ............................. 178

    Figure 5.1 The shrimp value chain in Thailand ........................................................... 202 Figure 5.2 Country of origin and gender of shrimp farm workers surveyed.............. 221 Figure 5.3 Previous occupation of shrimp farm workers .......................................... 222 Figure 5.4 Country and gender distribution of workers’ occupation prior to

    shrimp farm work ................................................................................................ 223 Figure 5.5 The ages of workers in shrimp farms interviewed for the survey. ........... 233 Figure 5.6 Basic steps for registering migrant workers ............................................. 240 Figure 5.7 Recruitment pathways for migrant workers ............................................ 247 Figure 5.8 Main areas of communication and interaction by farm scales ................ 259 Figure 5.9 Main areas of communication and interaction by origin ......................... 260

    Figure 6.1 The main elements in sustainable seafood production and trade ........... 285 Figure 6.2 Responses of farmers according to their educational level on

    the future involvement of their children ............................................................ 296 Figure 6.3 Previous occupations of survey respondents ............................................ 298 Figure 6.4 Sustainability factors ranked no. 1 by shrimp producers .......................... 299 Figure 6.5 Sustainability factors ranked no. 1 by tilapia producers ........................... 300

  • xii

    Figure 6.6 Sustainability factors cited most frequently by other stakeholder groups .................................................................................................................. 303

  • xiii

    LIST OF TABLES

    Table 2. 1 Shrimp production/farm scales ................................................................... 20 Table 2. 2 Tilapia pond production/farm scales ........................................................... 21 Table 2.3 Topics covered in the IFS questionnaires .................................................... 29

    Table 3.1 A summary of milestones in the aquaculture industry in Thailand relevant to the four target species ....................................................................... 43

    Table 3. 2 Number of aquatic feed mills and their original activities .......................... 71 Table 3. 3 Constraints faced by processing plants in exporting their products ........... 78 Table 3. 4 Classification of forms of exports by species ............................................... 79 Table 3. 5 The number of plants processing various species for export ...................... 80 Table 3. 6 Number of cold storage facilities and scope of activities ............................ 86 Table 3. 7 Definition of shrimp farming systems ......................................................... 95 Table 3. 8 Strengths and weaknesses of Thailand tilapia for export ........................... 98 Table 3. 9 Stakeholder analysis matrix (aquaculture global value chain in Thailand) . 99

    Table 4. 1 Study sites with corresponding number of farms by scale ....................... 113 Table 4. 2 Transition survey sample design ................................................................ 115 Table 4.3 General information on the global aquaculture standards used

    in this study ......................................................................................................... 118 Table 4. 4 Summary of standards for shrimp and tilapia farms based on global

    certifiers for aquaculture that have relevance to this study. ............................. 120 Table 4. 5 Aquaculture standards by DoF, Thailand ................................................... 121 Table 4. 6 Certified status of shrimp farms surveyed ................................................ 122 Table 4. 7 Production characteristics of shrimp farms by farm scale ........................ 124 Table 4. 8 Production characteristics of tilapia pond and cage farms surveyed ....... 128 Table 4. 9 Production characteristics of tilapia pond polyculture with ≥ 3 species ... 129 Table 4. 10 Whether there was agreement or not regarding discharge of

    effluent with neighbours ..................................................................................... 143 Table 4. 11 Number of precautionary measures used by farms to avoid predation and

    poaching .............................................................................................................. 157 Table 4. 12 Summary of outcomes in relation to compliance criteria of certification

    standards ............................................................................................................. 167 Table 4. 13 Reasons for stopping tilapia farming temporarily ................................... 175

    Table 5.1 Responses in relation to labour changes in the shrimp farms ................... 211 Table 5.2 Information on farm owners and managers interviewed ......................... 214 Table 5.3 Information on shrimp farm workers who were interviewed ................... 215 Table 5.4 Key informants interviewed for worker issues, at their place of work ..... 219 Table 5.5 Perceptions of shrimp farm workers on their quality of life ..................... 224 Table 5.6 Reasons for workers’ perceptions of a better quality of life ..................... 225 Table 5. 7 Salaries and bonuses of shrimp farm workers according to farm scale .... 229 Table 5. 8 Benefits provided to shrimp farm workers ............................................... 231 Table 5. 9 Types of migrant workers hired in shrimp farms...................................... 239 Table 5. 10 Costs in the recruitment and registration of migrant workers............... 241 Table 5. 11 Opinions on keeping the original documents by employers .................. 242

  • xiv

    Table 5. 12 Types of contract agreements with workers .......................................... 245 Table 5. 13 Various ways to recruit shrimp farm workers ........................................ 246 Table 5. 14 Status of compliance to labour standards in shrimp farms .................... 252 Table 5. 15 Shrimp farm employers’ opinions on working with different

    nationalities ......................................................................................................... 255 Table 5. 16 Future plans of migrant workers after working in shrimp farms in

    Thailand ............................................................................................................... 263

    Table 6. 1 Number of value chain actors interviewed/visited/met during the scoping research .......................................................................................... 290

    Table 6. 2 Important sustainability factors according to ranking by shrimp farmers ................................................................................................................ 299

    Table 6. 3 Important sustainability factors according to ranking by tilapia farmers ................................................................................................................ 301

    Table 6. 4 Sustainability factors most cited by respondents from different stakeholder groups ............................................................................................. 305

    Table 7.1 Summary of sustainability issues for shrimp and tilapia ............................ 331

  • xv

    LIST OF ACRONYMS

    ACFS Agricultural Commodity and Food Standards

    AEC ASEAN Economic Community

    AHPND Acute Hepatopancreatic Necrosis Disease AIT Asian Institute of Technology

    ASC Aquaculture Stewardship Council

    ASEAN Association of Southeast Asian Nations

    BAAC Bank of Agriculture and Agricultural Cooperatives

    BAP Best Aquaculture Practices

    CoC Code of Conduct CP(F) Charoen Pokphand (Foods)

    CSR Corporate Social Responsibility

    DO Dissolved Oxygen

    DoE Department of Employment

    DoF Department of Fisheries DLPW Department of Labour Protection and Welfare

    EEZ Exclusive Economic Zone

    EM Effective Microorganism

    EMS Early Mortality Syndrome

    EU European Union FAO Food and Agricultural Organisation of the United Nations

    FCR Feed Conversion Ratio

    FMD Fisheries Movement Document

    FW Freshwater

    GAA Global Aquaculture Alliance GAP Good Aquaculture Practices

    GVC Global Value Chain

    HS Harmonized System (Harmonized Commodity Description and Coding System) for traded products

    IFS Integrated Farm Survey ILO International Labour Organisation

    IPEC International Programme on the Elimination of Child Labour

    KI Key informant

    LPG Liquefied Petroleum Gas

    MOL Ministry of Labour MOU Memorandum of Understanding

    NACA Network of Aquaculture Centers in Asia and the Pacific

    NET Northeast Thailand

    OECD Organisation for Economic Co-operation and Development

    PCR Polymerase Chain Reaction

    PE Polyethylene PFO Provincial Fisheries Office

    PLs Postlarvae

    ppt Parts per thousand

    QOL Quality of Life

    RASFF Rapid Alerts System for Food and Feed SEAT Sustaining Ethical Aquaculture Trade

    SPF Specific Pathogen Free

    SPR Specific Pathogen Resistant

    SSP Sustainable Shrimp Programme

    TAO Tambon (sub-district) Administrative Organisation TFFA Thai Frozen Foods Association

    WSSV White spot syndrome virus

    YHV Yellow head virus

  • 1

    1. CHAPTER 1 Introduction

    1.1. Rationale / Problem statement

    Aquaculture is becoming more important in supplying the world’s demand for seafood

    (FAO, 2012) and Thailand has become a major player in seafood production, processing

    and international trade. Strategies for aquaculture production and trade have been

    created through government and private sector efforts to ensure sustainable production

    and trade for food security. On the other hand, markets and consumers have set

    standards and certifications to ensure good quality seafood grown in a sustainable

    manner, with the aim to guide producers and make consumers confident in their choices

    (Bostock et al., 2010). Bush et al. (2013) have argued though that aquaculture

    certification is just one of the many approaches to achieve sustainable production and

    that it could lead to a divide between larger scale and smaller scale farms in terms of

    ability to comply. Similar concerns have been voiced previously for example by Belton et

    al. (2011) regarding Pangasius aquaculture in Bangladesh and Vietnam. In fact, third-party

    certification could be more of a power and politically-driven process (Konefal and

    Hatanaka, 2011) which could affect compliance because not all farms are homogeneous.

    This brings us to the issue of sustainability, and how it is defined. Bell & Morse (2008) had

    pointed out that even though sustainability is a popular concept there is no specific

    definition of the word. They further added that since people do not live in similar

    conditions vis-à-vis environmental, social, and economic, it would not be right to just have

    one definition of sustainability. The word could mean differently to various people,

    depending on their own value systems (Bremer et al., 2013). On the other hand, a general

    overview of the term was provided by Robertson (2014), saying that “sustainability refers

  • 2

    to systems and processes that are able to operate and persist on their own over long

    periods of time.” Thus it is necessary that the perceptions of sustainability of various

    stakeholders is known and understood among themselves and between producers and

    consumers, and the intermediaries of the value chains that connect them.

    Sustainable development of export-orientated farmed seafood in Thailand is an issue that

    covers various aspects. It is not just the environmental or technical aspects or impacts of

    the aquaculture farms that should be factored in, but also the economic and social

    aspects, and the impacts and interactions, including the costs and benefits of all these

    aspects (L. Lebel et al., 2009; Lebel et al., 2002; Whitmarsh and Palmieri, 2009). As an

    example, Lebel et al. (2002) suggested that Thailand’s highly intensive (black tiger) shrimp

    production systems as well as “complex organizational structure” could not really be

    considered sustainable, and called for changes in modes of production, distribution,

    processing and governance (Lebel et al., 2002). Furthermore, it has to be noted that the

    concept of needs for, and limitations of, resources are core aspects for defining

    sustainability (WCED, 1987). There is a question of whose responsibility it is to achieve

    sustainable development in aquaculture. Actors directly and indirectly involved in

    aquaculture value-chains may lack a broader understanding of sustainability beyond their

    own concerns or business interests. Individual stakeholders do not necessarily share the

    same perspectives, even those coming from the same value chain node. There could be

    many factors within and outside their own systems which could affect their perceptions

    leading to different efforts in responding to these factors to make their operations

    sustainable. Therefore an improved or shared understanding of sustainability would

    enhance and/or accelerate a drive to more sustainable practices.

  • 3

    In order to focus efforts to achieve sustainable seafood production and trade to benefit

    both producers and consumers in Thailand and abroad, it is important to determine who

    the key stakeholders are, what they think about the sustainability of their operations,

    how different or similar are these perceptions are with each other, and what they are

    doing to improve sustainability. Looking at sustainability with its many facets requires a

    transdisciplinary approach, wherein various disciplines merge together to come up with a

    workable solution for the society, with a combination of qualitative and quantitative

    methods (Brandt et al., 2013).

    This study was more focused on farms, therefore it was necessary to classify farms in

    order to differentiate them. The main classification, aside from primary species cultured,

    was farm scale. During key informant interviews to determine the number of farms

    according to farm scales in the area, the respondents based their classification of ‘farm-

    scale’ by simply responding according to the size or area of farm. Farm scale is usually

    based on size or area of the farm while other factors that indicate scale of farm

    operations are not considered, such as labour, farm ownership and management (Murray

    et al., 2011). Thus for the purpose of this research, the SEAT project developed its own

    criteria for farm scaling to cover these factors. The details on farm scales used in this

    research are explained in Chapter 2.

    Due to the growing importance of and interest in certification and standards especially in

    global trade (Steering Committee of the State-of-Knowledge Assessment of Standards and

    Certification, 2012; Washington and Ababouch, 2011), the level of compliance of farms

  • 4

    could affect their participation in trade. Compliance to standards may be affected by the

    scale of operation of the farms, in that larger scale farms may be more likely to comply

    than smaller scale farms. The direct impact of compliance to standards is improvement in

    the production practices of the certified entity, which could also impact positively its

    external environment including other stakeholders (Steering Committee of the State-of-

    Knowledge Assessment of Standards and Certification, 2012). In the case of coffee,

    compliance to standards resulted in an “overall income impact” as well as “spill-over

    effects on adjacent communities”, although at the same time there were also weaknesses

    such as hidden costs and hindrances to trade (Giovannucci and Ponte, 2005).

    1.2. Labour issues

    Aquaculture production and trade in Thailand is providing employment, and thus

    contributing to food security both domestically and globally. With sustainability being

    linked with human dignity and the quality of life (van Egmond & de Vries, 2011), it is also

    a main issue to focus on the lives involved in aquaculture operations. Recently there has

    been a lot of attention to labour issues in shrimp aquaculture, and the quality of life or

    well-being of those employed in the sector. A number of case studies and reports have

    been presented regarding the situation outside the fish/shrimp farming sector i.e.

    upstream with the capture fisheries and downstream with the pre-processing and

    processing sectors, with the labour abuses and exploitation, child labour, and human

    trafficking issues, especially with migrant workers from neighbouring countries of

    Cambodia, Lao PDR and Myanmar (Derks, 2013, 2010; EJF, 2013a, 2013b; ILO, 2013a;

    ILRF/WWU, 2013; Sakaew and Tangpratchakoon, 2009; US Department of State, 2013;

    Vartiala et al., 2013). In most of the cases mentioned above, writers referred to the

  • 5

    “shrimp farming industry” as a whole. However, there is not much information being

    reported on the labour situation at the farm level except recently by Resurreccion & Sajor

    (2010 and 2011) which was specific on gender aspects. Even ILO in Thailand had

    mentioned that the risk of labour abuse at the farm level may be lower than that in the

    factories and processing plants (Toumo Poutiainen, personal communication, 2013), and

    acknowledged that this conclusion was based more on anecdotal evidence rather than

    data. A report on child labour i.e. children involved in economic activities, in selected

    areas in Thailand related to aquaculture was published recently by ILO/IPEC project and

    confirmed the existence of child labour in those specific areas, in fisheries and

    aquaculture (ILO, 2013a).

    A total of 11.71 M workers as of early 2014 were reported in Agriculture, Forestry and

    Fishery sectors (MOL, 2014). In addition, the Ministry of Labour reported that there were

    1,211,104 legal migrant workers, and 23,391 illegal migrant workers. The migrant to

    employed workers ratio was 2.93% in 2013 (MOL, 2014). This records the documented

    workers and does not specify how many are working in the aquaculture sector, more so in

    farms. Kruijssen et al. (2013) estimated less than 1% of the total workforce (Thai and

    migrants) are involved in the fishing, farming and processing sectors, and does not

    include the workforce in fish markets.

    It has been estimated that there are about 1 million people involved in the shrimp

    industry sector (Songsangjinda and Smithrithee, 2008; Tanticharoen et al., 2008),

    however, there are no specific numbers of people employed in aquaculture farms. In the

    Department of Employment, the number of registered migrant workers in aquaculture is

  • 6

    recorded under the agriculture and livestock category. There is a separate category for

    fisheries sector but this refers to work on capture fishing vessels. Thus there are no

    reliable figures to estimate the total number of workers in the shrimp and fish farming

    sector.

    Species-specific global standards and certification for aquaculture farms also include the

    community and human resources aspects, focussing on working conditions of the workers

    such as worker safety, employee relations, corporate social responsibility and responsible

    social practices (ASC, 2014, 2012; GAA-BAP, 2013; GlobalGAP, 2012, 2011). It does not

    take into consideration other aspects which are not directly related to the work, such as

    informal work contribution by a family member or employment of couples, which are

    important considerations for workers living on-farm. Issues regarding the quality of life of

    workers and families, and relationships, therefore gender issues, and their living and

    working conditions in the farms need to be considered. The OECD’s Better Life Initiative

    (OECD, 2013) may be useful if it is applicable to sectoral or value chain node evaluation of

    well-being. Another useful approach is that of Costanza et al. (2007) and Petrosillo et al.

    (2013) which suggested to incorporate aspects of opportunities, human needs and one’s

    perceptions of well-being.

    The issue on the importance of migrant labour in the shrimp sector leads us to the

    question of why there is such a degree of dependence and the issue of the relative

    absence of Thai workers (ARCM/IAS/CU, 2013; Human Rights Watch, 2010; ILO, 2013a;

    Resurreccion and Sajor, 2010). Whereas in the past, there was local migration mainly

    from northeastern provinces to work in shrimp farms in the east and south, the situation

  • 7

    appears to have changed considerably (Resurreccion and Sajor, 2011). Local migration

    was common among northeastern Thais in search of better incomes to survive the

    poverty in their region (Ekachai, 1990) and this was the reason to drive them to work in

    many available occupations in other regions in Thailand. Rigg & Nattapoolwat (2001)

    reported the loss of labour from rice farming to more lucrative jobs in orchards and

    factories.

    1.3. Gender issues

    Value chain actors are in constant interaction with each other, to transact business, for

    business networking, and for family and social activities. In analysing these interactions, a

    gender perspective is necessary in order to guide the framework of evaluation of the

    impacts of international trade on gender relations among value chain actors in selected

    countries in Asia. Gender refers to the social differences between men and women, boys

    and girls, which are determined by society and may be learned and changed, and could

    vary between and within cultures (FAO, 2001; GGCA, 2009). As noted by Laven et al.

    (2009), most tools and interventions lean toward non-gender sensitiveness in working

    with value chains and rural livelihoods, thus they have attempted to create a trajectory

    on gender in value chains by combining gender and women empowerment with value

    chain/pro-poor development.

    The export of seafood from producing countries has increased considerably over the last

    two decades, for selected species such as shrimp in Thailand. Despite the high value

    earnings from foreign trade, there remains a vibrant domestic market demand for other

    species namely tilapia and freshwater giant prawn. The intensity of labour use along the

  • 8

    value chains varies between countries and among species, and although both men and

    women may be present in each value chain node, there are roles which have been

    specific to each gender based on their ability, culture and skills, and benefits could be

    different between genders (UNRISD, 2012). Moreover, UNRISD also reported about

    disparities in benefits between men and women along the value chains, not only in

    aquaculture but in general employment. The same trend could be seen in non-timber

    forest products in Africa wherein women face many obstacles to participate in economic

    activities (Shackleton et al., 2011). In addition, Laven and Verhart (2011) also pointed out

    that women worked in parts of the value chain which have lower values, thereby getting

    lower benefits compared to men.

    In Thailand shrimp processing plants for example, women are usually involved in work

    needing skills and detail such as filleting and deveining, while men were delegated to

    heavy lifting tasks, driving and machinery work. In Bangladesh, >40% of fry catchers were

    women and girls and > 60% of workers in the processing plants were women (USAID,

    2006). In Vietnam and Nigeria, women are more visible in growout/farming, processing

    and marketing, rather than in hatcheries (Veliu et al., 2009).

    The gender aspect is a cross-cutting theme in this research, as this study deals with not

    only the physical aspects of aquaculture but also assesses the human aspects through

    their roles and interactions as stakeholders, value chain actors and workers.

    Understanding gender is also important in well-being studies (OECD, 2013). The

    promotion and implementation of gender equality in aquaculture are critical for any

    contribution of the sector to the Millennium Development Goals (MDGs) (Arenas and

  • 9

    Lentisco, 2011). Although implementing a comprehensive gender analysis is problematic

    in most research contexts, integrating gender aspects into a broader social and economic

    analysis can contribute to an understanding of how male and female actors’ needs could

    be addressed and met, for e.g. finances, decision making, information, and actual tasks

    (Lebel et al., 2009). In this way, each actor will not lose opportunities for advancement

    and their access to resources to develop themselves and improve their quality of life

    (Pryck, 2013).

    1.4. Brief information about the SEAT project

    The Sustaining Ethical Aquaculture Trade (SEAT) Project was implemented under the

    Framework Program 7 of the European Commission, under a research consortium of 13

    institutional partners from Europe and Asia. The SEAT project was conceptualised during

    the period of rising global consumption of seafood and associated trade volumes due to

    an increasing population, increased wealth and changes in the eating habits of

    consumers. With more than half of the seafood traded internationally, from developing

    to developed countries, there has been a growing concern by markets and consumers

    regarding how the processes along the global value chains for seafood meet standards for

    sustainable food production and trading. The SEAT Project looked at the four key species

    groups namely the river catfish (Pangasiidae), freshwater river prawns, marine shrimp,

    and tilapias in Asian countries namely Bangladesh, China, Thailand and Vietnam. The

    development and intensification of farming systems of these species have raised serious

    concerns regarding the sustainability of the practices involved and the overall trade. The

    project aimed to establish an evidence-based framework to support current and future

    stakeholder dialogues organised by third party certifiers, which could contribute towards

  • 10

    harmonized standards, helping consumers to make fully informed choices with regards to

    the sustainability and safety of their seafood. The project ran from 2009 to 2013, taking a

    highly interdisciplinary approach to address sustainability questions. Topics addressed

    included environmental impacts, impacts of trade on local livelihoods and public health,

    food safety including contaminants and traceability concerns, barriers to trade, and

    ethics. Life cycle analysis was used to explore energy and material costs embedded in the

    global value-chains, while food ethicists examined the value-laden nature of sustainability

    decisions i.e. who decides which qualities are significant in relation to sustainability. This

    thesis is concerned with the Thailand aspect of the project. The information in this section

    on SEAT Project was summarised from project documents (SEAT, 2009).

    1.5. Research objectives

    The main objective of the study was to assess the sustainability issues faced by various

    value chain actors, specifically shrimp and tilapia producers, based on their own

    perceptions.

    Specifically, the study aimed to:

    1. Describe the historical development of aquaculture and the status of the four

    commercially important seafood species (marine shrimp, tilapia, freshwater

    prawn, striped catfish) in Thailand and assessing the factors contributing to their

    importance in international and domestic markets (Chapter 3)

    2. Analyse shrimp and tilapia farming systems according to the farm-level criteria of

    global standards and certification to determine status of compliance between

    farming enterprises of various farm scales (Chapter 4)

  • 11

    3. Assess the quality of life of shrimp farm workers according to their perceptions

    and investigate the status of compliance to global standards for human resources

    in aquaculture (Chapter 5)

    4. Show the differences in perceptions on sustainability of various value chain actors,

    and specifically, among producers according to farm scale and other relevant

    variables (Chapter 6)

    1.6. Key concepts/theoretical framework

    The transdisciplinary nature of sustainability studies ensures that they are both complex

    and varied in terms of approach. Figure 1.1 shows the general framework followed by this

    research, namely:

    Scoping and exploratory approach to obtain an overview of the historical

    development and existing systems related to the four major species in this

    research, i.e. marine shrimp, tilapia, freshwater prawn and striped catfish in

    relation to the various stakeholders involved. This led to focus species that are

    important to and have potential for export and trade, namely marine shrimp and

    tilapia, respectively. This also led to identify system boundaries and stakeholders

    who would participate in the more detailed research;

    Integrated farm survey approach was conducted to obtain more detailed

    information on production systems (farm level) of the focus species, i.e. marine

    shrimp and tilapia, covering technical, economic, social and ethical issues. Also

    includes determining producers’ perceptions on sustainability of their operations

    to contribute to the development process for sustainability indicators for the

    overall SEAT Project. In addition, several aspects of farm operations were

  • 12

    compared with the global certification standards to determine compliance

    according to farm scales;

    State of the system workshop approach to present preliminary findings for

    triangulation with a group of integrated farmer survey respondents and

    representatives from other relevant stakeholders (input service providers,

    hatchery operators, processors, institutions, local government and academe),

    including to obtain their perceptions on sustainability, which will also contribute

    to the development process for sustainability indicators for the overall SEAT

    Project;

    Transition survey approach to determine changes in the farm operations of a

    sample of respondents from the integrated farm surveys, and also to determine

    samples for labour face to face survey;

    Face to face surveys related to detailed issues on shrimp farm labour and

    workers’ welfare, with particular interest on migrant labour in shrimp farms; and

    to measure the existing farm conditions with the labour standards as well as

    workers’ own perceptions of their quality of life;

    Future steps stemming from this research: more information gathering on data

    gaps, development of the sustainability indicators, dissemination of relevant

    information, action research and policy advocacy, among others.

    A multi-stage livelihoods approach was employed, keeping in mind the three main facets

    of sustainability, i.e. environmental, economic and social or institutional. In the

    sustainability and quality of life aspects of this research, information relied mainly on the

    perceptions of various stakeholders.

  • 13

    As a starting point to analyse sustainability of farms and the link with farm scales, various

    aspects of the aquaculture global standards and certifications were used as benchmarks.

    In addition, a simple gender dimensions framework was incorporated into the approach

    especially in formulating questions in the surveys to obtain gender-disaggregated data.

    Figure 1.1 The general research framework

    1.7. Structure of thesis

    This thesis contains seven major chapters, the first being the Introduction, and the last

    being the Overall Discussion and Conclusions, and the remaining five chapters contain the

    main parts of the research.

    Future steps

    & labour patterns

  • 14

    Chapter 2 describes the general methodology followed in this research, especially

    regarding the sample frame and design to determine study sites and survey respondents.

    Subsets of these survey respondents were selected to provide information and

    interaction in the other chapters.

    Chapter 3 provides a systems overview of the four commercially important farmed

    seafood species (marine shrimp, tilapia, freshwater prawn and striped catfish) in Thailand,

    assessing the factors that contribute to their emergence as internationally traded

    products or their restriction to domestic markets. This chapter provides the rationale for

    focussing on shrimp and tilapia in this research.

    Chapter 4 provides a detailed analysis of shrimp and tilapia production practices in

    Thailand as well as the changes and trends. The chapter focusses on how the production

    sector operates in order to fulfil both local and global demand for Thai seafood, including

    the changes the sector has to face to achieve this. Current practices are presented using

    the technical and legal aspects of international standards and certifications as a

    framework. Changes and trends in the sector are assessed to understand likely threats to

    sustainability of farming and the sector as a whole.

    Chapter 5 focusses on the human resources and gender aspects of shrimp farming in

    Thailand. The analysis focusses on how shrimp farms comply with the human resource

    aspect of the global aquaculture standards and certifications, to determine whether these

    standards are suitable in assessing the quality of life of shrimp farm workers, and to

    compare them with the workers’ own perceptions of their quality of life.

  • 15

    Chapter 6 is about the sustainability perceptions of shrimp and tilapia stakeholders,

    particularly the producers, analysing how different their perceptions are according to

    farm scales and other variables, and how these producers are managing or changing their

    operations to make the most of the situation. Having said that, there could be differences

    in sustainability perceptions by the various stakeholders, or even by different types of

    farmers, this may also mean that the definition of sustainability may be different from

    one person to another, depending on the context and situation.

  • 16

    2. CHAPTER 2 General Methodology

    This research involved connecting and interacting with actors/stakeholders across the

    value chains of shrimp and tilapia production, processing and trade. The majority of the

    data obtained were from the production node, i.e. the producers or farmers. Various

    sources of information were used to build the general sample frame, on which selection

    of survey respondents were based for subsequent field work. The general sample frame

    of the whole study was based on census data obtained from local fisheries offices,

    subdistrict administration offices, village chiefs, shrimp club offices and informal data

    from key informants within individual communities, and additional secondary literature

    from national government statistics, associations and company information.

    This research was part of a bigger collaborative project called Sustaining Ethical

    Aquaculture Trade (SEAT) funded by the European Commission under its FP7 Programme.

    I have been actively involved in the design, planning and implementation of the various

    phases of the research mentioned below which concerned the data collected for this

    doctoral dissertation.

    2.1. Research activities

    This study involved four major research activities in connecting and interacting with

    stakeholders from 2010 to 2013, which provide the data and information for the various

    chapters of this thesis (Figure 2.1). This chapter presents the main sample frame, study

    site selection and farmer selection which formed the basis for all the other subsequent

    research activities involving the same sets of respondents. The various chapters in this

    thesis will detail relevant methods to obtain data for that specific chapter.

  • 17

    Figure 2.1 Major research activities and timeline undertaken to collect field data

    The first activity was an exploratory scoping exercise to assess the export potential and

    domestic market status of the four cultured seafood commodities (marine shrimp, tilapia,

    freshwater prawn, and striped catfish) in Thailand. This was done mainly through key

    informant interviews and secondary literature search. In addition, both methods were

    also used to identify key stakeholder groups and obtain a general overview of the

    situation of each, including their perceptions on sustainability. This was conducted from

    January to July 2010 using a checklist of questions (Appendix 2) covering issues which

    SEAT Project was interested in. The results contributed to both the systems overview

    (Chapter 3) and sustainability systems (Chapter 6) sections. Key informant interviews

    were done through individual field visits and meetings with identified stakeholders,

    attendance to producers’ seminars, and organising workshops attended by various

    stakeholder groups. The scoping stage was also used to define system boundaries for

    focus species to be used for subsequent research works.

    Jan-Jul 2010 Nov 2010 – Mar 2011 Mar – May 2013 Apr – May 2013

  • 18

    The second activity was an integrated farm survey (IFS) focusing on producers of shrimp

    and tilapia from major production areas in Thailand, with more detailed questions on

    operations and practices, sustainability, generational factors, including socio-economic

    information related not only to their aquaculture operations but also to their household

    circumstances (Appendix 4). This provided information to all the work packages of the

    SEAT project. The survey itself was conducted from November 2010 to March 2011, with

    the sample design and selection of sites guided by the results of the scoping stage to set

    system boundaries. A multi-stage sampling process was followed, starting from larger

    (province) then progressing to smaller (district, sub-district, village) administrative units

    (Murray et al., 2011). Furthermore, various datasets on farm locations, farmer names,

    farm scales and farming systems, from key informant interviews and secondary literature

    research during the scoping period were used to derive the location for study sites and

    farms (see Section 2.2 for detailed description). Preparation for the survey started in July

    2010 until November 2010. The methodology on selection of sites and respondents is

    explained in this chapter (Chapter 2). More detailed descriptions relevant to the chapters

    utilising data from the integrated survey are described in specific chapters i.e. current

    practices and trends in Chapter 4, respondents’ background in Chapter 5, and

    sustainability perceptions in Chapter 6.

    A state of the system workshop was conducted as a continuation of the IFS, expanding to

    include a sample of other value chain actors. The information from this activity also

    contributed to the sustainability perception in Chapter 6. Details of the SOS workshop are

    reported in Satapornvanit et al. (2011).

  • 19

    The third activity was a transition survey (Appendix 5) conducted by phone in March 2013

    for shrimp farmers, and in April to May 2013 for tilapia farmers, i.e. 2-3 years after the

    baseline integrated farm survey was conducted. The purpose was to assess key changes

    that had occurred in farming operations and in the general situation of the farm business

    operations and personal status of the integrated survey respondents. A detailed

    methodology is presented in Chapters 4 and 5.

    The fourth activity was a face to face survey of shrimp farmers, workers and key

    informants on labour patterns from April to May 2013 based on the results of the

    transition phone survey among shrimp farmers (third activity) (Appendix 6, Appendix 7).

    A detailed methodology is explained in Chapter 5.

    2.2. Sample frame

    Definitions of farm scales were developed together with the other members of the SEAT

    project team and formed part of a regional four country exercise. My involvement was to

    provide inputs and information based on local conditions that were relevant to country-

    specific criteria. The information came from previous scoping research and general

    industry information. The definitions of the criteria used are explained below.

    Shrimp farm samples were based on production scales, i.e. small, medium and large

    (Table 2.1).

  • 20

    For tilapia, sampling was based on containment system (cages in river, ponds) at the first

    instance, and under each system, tilapia ponds were divided into production scales, i.e.

    small, medium and large (Table 2.2). The production scale for tilapia in cages was difficult

    to determine as the scoping study indicated that a single farming household, or individual

    within it, can manage the whole operation by themselves over a very large range of

    production containment systems (from 1 to 100 units). The farmer interviewed during

    scoping phase who had the most number of cages (100 units @ 9 m2 x 1.5 m/unit) was

    producing around 600 T/year, hiring labour only for harvesting the fish. Whereas the

    farmer with only one cage (25 m2 x 2.5 m) was producing 3.8 T/year. During this research

    all farms with cages were not subjected to scaling. The criterion for large farms i.e.

    registered company with vertical integration was still applied, and there was only one

    tilapia farm (ponds) in the study area which fit this criterion, and none for cages.

    Farm scaling for cages needs a different set of criteria which was not covered in this

    research, maybe based on production intensity/levels per unit area.

    Table 2. 1 Shrimp production/farm scales

    Criteria Small Medium Large

    No. of ponds Up to 2 3 and above N.A.

    Business ownership Household/extended

    family

    Household/extended

    family/external owner

    Company/corporate

    Farm management Household/extended

    family

    Household/extended

    family/external owner

    /hired manager

    Hired manager

    Labour relations Up to 2 hired full-time

    labour

    3 and above hired full-

    time labour

    Hired employees/

    full-time labour

    Source: Murray et al. (2011)

  • 21

    Table 2. 2 Tilapia pond production/farm scales

    Criteria1 Small Medium Large

    Area of farm Up to 2 has (12.5 rai) > 2 has. N.A.

    Business ownership Household/extended

    family

    Household/extended

    family/external owner

    Company/corporate

    Farm management Household/extended

    family

    Household/extended

    family/external owner

    /hired manager

    Hired manager

    Source: Murray et al. (2011)

    2.3. Definition of farm scale criteria

    As stated in Murray et al. (2011), the farms were categorized by scales according to

    indicators which relate to their market orientation rather than production output alone.

    During farm selection and surveys, these indicators were considered and were confirmed

    with key informants and the farmers themselves.

    Business ownership: The majority of farms are owned by individual persons, who assume

    full-time management of the aquaculture operations and/or hire an external individual to

    handle the management. Corporately owned farms are registered as a company with the

    Department of Business Development, Ministry of Commerce. A number of “traditionally

    large farms” based on farm size and operations, fall under the medium scale criteria since

    they are not registered as a company. Major reasons cited by respondents for not

    registering as a company include the paperwork and documentation required, as well as

    tax level payments.

  • 22

    Farm management: Depending on scale, farms are managed by the owner herself/himself

    or household member, i.e. partnership with the married couple owners or with the adult

    children, or by external person hired as a manager.

    Full-time waged labour: Even those considered small farms may also hire full-time labour,

    especially if the owner is considered an absentee owner, or have other livelihood

    activities or business interests. Workers are usually assigned responsibility for one pond,

    workers employed as a couple typically manage two ponds. Nowadays, due to

    mechanisation i.e. paddlewheel aerators and autofeeders, a worker may be able to

    handle two ponds on his own, especially if experienced.

    In tilapia farms, labour requirements are lower. For cage farms, a single person can

    handle up to 100 cages (usually 9 m2 in area) and would just hire part-time workers to

    help in harvesting.

    Registered trading name: In Thailand, any aquaculture farm can register with the

    Department of Fisheries. Registration is prerequisite for the traceability system involving

    the Fisheries Movement Document (FMD) which is needed for exporting product. Other

    types of aquaculture farms are also registered for the Thai Good Aquaculture Practices

    (ThaiGAP) certification, as well as for annual fisheries statistics and disaster or welfare

    benefits. Thus when disaster such as flooding occurs, farms registered with DoF can seek

    government financial support. In addition, farms may register with the Department of

    Business Development to be recognised as a corporate entity.

  • 23

    Vertical and horizontal integration: Vertical integration occurs when the different

    stages/processes (i.e. from production to delivery) in the value chain is

    coordinated/controlled/owned by one lead company or entity, which results in increased

    efficiency and market power for that company. This could also be achieved through

    agreements and written contracts with various actors/owners of processes, or being

    involved in several activities in the value chain (GTZ, 2007; Laven et al., 2009). Larger

    farms tend to have more integration of the production chain in order to minimise cost

    and improve quality of production. This improves traceability of processes and inputs into

    the production. Whereas horizontal integration in the farming sense occurs when one is

    involved in the management issues including decision making in the chain (Laven et al.,

    2009).

    2.4. Selection of study areas

    There were two major steps in the selection process for the study areas, namely the

    selection of provinces and then the sub-districts (tambon). This process utilized secondary

    data from the Department of Fisheries (DoF) and the Provincial Fisheries Offices (PFO).

    The provinces were selected based on the number and area of registered farms including

    accessibility from the Bangkok research base and the availability of support from local

    Government offices, farmer groups and individual key informants.

    Information from the DOF national fisheries statistics showing major areas of production

    was also used as reference. Due to limitations in resources, time and accessibility, only

    tilapia production areas in the central region were considered. Based on the DoF

    statistics, the most productive provinces were Nakhon Pathom, Chachoengsao and

  • 24

    Petchburi for freshwater pond polyculture systems, and Suphanburi for monoculture

    cages in river systems.

    In contrast the most productive areas for shrimp were in the two major coastal regions,

    i.e. the east and the south. For the eastern region, two provinces namely Chachoengsao

    and Chanthaburi were chosen, while in the south, Surat Thani was chosen. These

    provinces ranked among the top for production levels, number and area of farms as well

    as accessibility considering resources of the project for those particular regions (Figure

    2.2). Other southern provinces, namely, Nakhon Sri Thammarat, Songkhla and Satun were

    later included as additional large farms were needed.

    Figure 2.2 Provinces where the surveys were conducted

  • 25

    After selecting the provinces, the number of farms in the sub-districts (based on

    information obtained from local Department of Fisheries) was sorted from highest to

    lowest, and only those with more than 50 farms were subjected to a randomisation

    process (Gentle, 2003) using the equation in MS Excel: = RAND( ) * (MAX(cell1:celln)-1) + 1,

    where, cell1 is the first value in the column and celln is the last value in the same column

    (Murray et al., 2011). The values are the cumulative number of farms in each sub-district

    (after ranking from highest to lowest).

    2.5. Farmer sampling

    Obtaining a complete list of producer households/farm owners was not possible as this

    information was subject to the Official Information Act, B.E. 2540 (1997) of Thailand (Thai

    Royal Gazette, 1997), whereby any personal information requested required a written

    request and written permission of all farm owners/operators whose information was

    accessed.

    An initial list was obtained from published farmers’ lists from DoF websites, local fisheries

    offices and key informants from the areas sampled randomly (see Section 2.4). An initial

    categorisation was based on these lists, after which farms were categorised according to

    scale to ensure adequate numbers of small and medium farms, based on the available

    information. However information especially on labour, was not enough to completely

    categorise them using the classification given above (Tables 2.1 and 2.2).

    The second categorisation was based on key informant interviews (KIIs) in the field. Key

    informant interviews were conducted to obtain a more detailed overview of the situation

  • 26

    of shrimp and tilapia farms in specific areas (Appendix 3). The initial categorised farmer

    lists were validated by going to at least three key informants (sub-district administrative

    organization (TAO) offices, the local farmer club and the village heads) in each selected

    sub-district. Missing farmers’ names were identified and added to the list, while farmer

    names from the secondary data were removed if they were no longer farming shrimp or

    tilapia. However, if the farm itself still existed but had a different business owner, it was

    still included in the list. Contact information of each identified farm was also obtained

    from the KIs. In cases where the contact information could not be given by the KIs due to

    confidentiality, the KIs were requested to contact the farms if ever they were randomly

    selected. In most cases the KIs could not provide information on hired labour status of the

    farms (which was one of the criteria to determine farm scales).

    From the KIIs, new lists were drawn up and clusters were identified based on sub-districts

    to ensure enough numbers of farms for selection. A randomised sample of households

    was then applied with the scale independent variable strata to achieve the sample design

    numbers. Randomisation using the Excel RAND formula was run on enterprise data after

    farms were categorised into their production/farm scales. The randomisation programme

    from MS Excel (= RAND( ) * (C1 - B1) + B1, where B1 is 1, and C1 is the highest number of

    farms) was run to determine the farmers to be interviewed (Murray et al., 2011).

    Initially, 200 shrimp and 200 tilapia farmers were sampled. However, due to reasons such

    as availability and willingness to participate, the final number of respondents for shrimp

    was 206 and for tilapia, 199.

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    2.6. Integrated farm surveys (IFS)

    Farmers who were randomly selected from the above processes were contacted by either

    field staff or KIs, depending on the availability of information and on the situation in each

    site. In most cases, it was the key informant or KI (such as the village headman, subdistrict

    head or his technical staff, or the local shrimp club head or his representative) who

    assisted in contacting the respondents. The KI would arrange for the respondents to come

    to a central place for the interviews to be conducted. Typically a local venue where

    farmers already met informally was chosen for such interviews. After the interviews, the

    farms were visited, and after permission was sought and given, GPS coordinates and

    photographs were taken to characterise location and key characteristics. A few interviews

    especially those organised directly by field research staff, were conducted in the farms

    depending on the respondents’ preferences.

    There were cases when some of the farms, especially large farms, requested an official

    letter from the Faculty of Fisheries, Kasetsart University. This has become standard

    protocol in Thailand and the SEAT project management assisted in preparing and

    procuring these letters to be sent to the farms/companies in the time period required by

    the respondents.

    Whereas the main target to interview were the farmers or farm owners, there were

    instances when only the farm managers of shrimp farms were available to be

    interviewed, especially in the case of some medium-scale farms and in all cases for the

    large (corporate) farms.

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    The interviews were conducted by a team of Thai field research assistants who were

    recruited and trained for several weeks prior to the scheduled interviews to familiarise

    themselves with the questions, aquaculture terminology, and coding of responses, as well

    as to have a basic understanding of shrimp and tilapia farming. Not all of the enumerators

    had fisheries or aquaculture backgrounds but they all had field survey experience with

    other non-aquaculture projects. Training sessions were conducted for either the whole

    day, or half-day (morning or afternoon) depending on other work load of the staff. Prior

    to the training, meetings related to questionnaire development were conducted, wherein

    the enumerator team was also present to observe and/or participate in the discussions

    (see Section 2.7). The final version of the translated (from English to Thai) questionnaires

    was used for the training, which was conducted in the Thai language. In addition, the

    accompanying notes developed by the SEAT project team (Murray et al., 2011) were also

    used as reference to explain the questions and choices of responses. The Thai training

    facilitator would clarify aquaculture specific topics or terms with me during and outside

    the training sessions. The team would go through each question and